首页> 外文期刊>Applied Geochemistry: Journal of the International Association of Geochemistry and Cosmochemistry >Attenuation of pyrite oxidation with a fly ash pre-barrier: Reactive transport modelling of column experiments
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Attenuation of pyrite oxidation with a fly ash pre-barrier: Reactive transport modelling of column experiments

机译:用粉煤灰预阻挡层衰减黄铁矿氧化:柱实验的反应传输模型

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摘要

Conventional permeable reactive barriers (PRBs) for passive treatment of groundwater contaminated by acid mine drainage (AMD) use limestone as reactive material that neutralizes water acidity. However, the limestone-alkalinity potential ceases as inevitable precipitation of secondary metal-phases on grain surfaces occurs, limiting its efficiency. In the present study, fly ash derived from coal combustion is investigated as an alternative alkalinity generating material for the passive treatment of AMD using solution-saturated column experiments. Unlike conventional systems, the utilization of fly ash in a pre-barrier to intercept the non-polluted recharge water before this water reacts with pyrite-rich wastes is proposed. Chemical variation in the columns was interpreted with the reactive transport code RETRASO. In parallel, kinetics of fly ash dissolution at alkaline pH were studied using flow-through experiments and incorporated into the model. In a saturated column filled solely with pyritic sludge-quartz sand (1: 10), oxidation took place at acidic conditions (pH 3.7). According to SO42- release and pH, pyrite dissolution occurred favourably in the solution-saturated porous medium until dissolved O-2 was totally consumed. In a second saturated column, pyrite oxidation took place at alkaline conditions (pH 10.45) as acidity was neutralized by fly ash dissolution in a previous level. At this pH Fe release from pyrite dissolution was immediately depleted as Fe-oxy(hydroxide) phases that precipitated on the pyrite grains, forming Fe-coatings (microencapsulation). With time, pyrite microencapsulation inhibited oxidation in practically 97% of the pyritic sludge. Rapid pyrite-surface passivation decreased its reactivity, preventing AMD production in the relatively short term.
机译:被动处理受酸性矿山排水(AMD)污染的地下水的常规渗透性反应性屏障(PRB)使用石灰石作为中和水酸度的反应性材料。但是,由于不可避免地会在晶粒表面发生二次金属相的沉淀,因此石灰石碱度电位停止,从而限制了其效率。在本研究中,对煤燃烧产生的粉煤灰进行了研究,它是使用溶液饱和柱实验对AMD进行被动处理的一种替代碱度产生材料。与常规系统不同,提出了在预屏障中利用粉煤灰拦截未污染的补给水,然后该水与富含黄铁矿的废物反应。色谱柱中的化学变化用反应性运输代码RETRASO解释。同时,使用流通实验研究了在碱性pH下粉煤灰溶解的动力学并将其纳入模型。在仅充满黄铁矿污泥-石英砂(1:10)的饱和柱中,在酸性条件下(pH 3.7)进行氧化。根据SO42的释放和pH值,黄铁矿在溶液饱和的多孔介质中的溶解良好,直到溶解的O-2被完全消耗掉为止。在第二个饱和塔中,黄铁矿氧化在碱性条件下(pH 10.45)进行,因为酸度通过粉煤灰的溶解被中和至先前水平。在此pH值下,黄铁矿溶解释放出的铁立即消失,因为铁-氧(氢氧化)相沉淀在黄铁矿晶粒上,形成铁涂层(微囊化)。随着时间的推移,黄铁矿微囊化实际上抑制了97%的黄铁矿淤泥的氧化。黄铁矿表面的快速钝化降低了其反应性,在相对较短的时间内阻止了AMD的生产。

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